Article
The design of long-term effective uranium bioremediation strategy using a community metabolic model
Article first published online: 26 APR 2012
DOI: 10.1002/bit.24528
Copyright © 2012 Wiley Periodicals, Inc.
Additional Information
How to Cite
Zhuang, K., Ma, E., Lovley, D. R. and Mahadevan, R. (2012), The design of long-term effective uranium bioremediation strategy using a community metabolic model. Biotechnol. Bioeng., 109: 2475–2483. doi: 10.1002/bit.24528
Publication History
- Issue published online: 21 AUG 2012
- Article first published online: 26 APR 2012
- Accepted manuscript online: 17 APR 2012 09:23AM EST
- Manuscript Accepted: 6 APR 2012
- Manuscript Revised: 30 MAR 2012
- Manuscript Received: 19 JAN 2012
Funded by
- Office of Science (BER), U.S. Department of Energy. Grant Number: DE-FG02-07ER64367
Keywords:
- community metabolism;
- metabolic modeling;
- optimization;
- bioremediation
Abstract
Acetate amendment at uranium contaminated sites in Rifle, CO. leads to an initial bloom of Geobacter accompanied by the removal of U(VI) from the groundwater, followed by an increase of sulfate-reducing bacteria (SRBs) which are poor reducers of U(VI). One of the challenges associated with bioremediation is the decay in Geobacter abundance, which has been attributed to the depletion of bio-accessible Fe(III), motivating the investigation of simultaneous amendments of acetate and Fe(III) as an alternative bioremediation strategy. In order to understand the community metabolism of Geobacter and SRBs during artificial substrate amendment, we have created a genome-scale dynamic community model of Geobacter and SRBs using the previously described Dynamic Multi-species Metabolic Modeling framework. Optimization techniques are used to determine the optimal acetate and Fe(III) addition profile. Field-scale simulation of acetate addition accurately predicted the in situ data. The simulations suggest that batch amendment of Fe(III) along with continuous acetate addition is insufficient to promote long-term bioremediation, while continuous amendment of Fe(III) along with continuous acetate addition is sufficient to promote long-term bioremediation. By computationally minimizing the acetate and Fe(III) addition rates as well as the difference between the predicted and target uranium concentration, we showed that it is possible to maintain the uranium concentration below the environmental safety standard while minimizing the cost of chemical additions. These simulations show that simultaneous addition of acetate and Fe(III) has the potential to be an effective uranium bioremediation strategy. They also show that computational modeling of microbial community is an important tool to design effective strategies for practical applications in environmental biotechnology. Biotechnol. Bioeng. 2012; 109: 2475–2483. © 2012 Wiley Periodicals, Inc.

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